Pharmacodynamics of dieldrin in pigeons

Organochlorine Pesticide Residues Among Colonial Nesting Birds in Tamil Nadu, India: A Maiden Assessment from Their Breeding Grounds

Use of pesticides continues to be indiscriminate, and birds are one of the worst affected non-targeted organisms. Information on the ill effects of pesticides on birds far from desired in India. Despite the presence of a wide variety and number of birds, there is exceedingly little data on organochlorine pesticide (OCP) residues in colonial nesting birds in sanctuaries of India. A total of 76 individuals belonging to 14 species of birds found dead between March 2008 and March 2010 were analyzed for pesticide residues in various tissues. Of all the OCPs analyzed, concentration of HCH was found to be the highest. Magnitude of contamination varied widely among species. Accumulation pattern of OCPs in colonial nesting birds was in the order ∑HCH > ∑endosulfan > ∑DDT > heptachlor epoxide > dieldrin. Pesticides, namely p,p-DDE and β-HCH contributed most towards the total OCPs. Concentrations of DDT and its metabolites, HCH and isomers, dieldrin, and heptachlor epoxide were lower than the concentrations reported for various species of birds elsewhere in India. Although the sanctuaries presently studied have official boundaries, physical demarcations are missing and there are no proper earthen dykes particularly in Vedanthangal and Koonthankulam Bird Sanctuaries. During monsoon, runoff not only floods the Sanctuaries but also the cultivated areas nearby. Run off brings in residues of pesticides and fertilizers from the agricultural lands into the sanctuaries. Although OCP results in this study were below threshold limits, it may be noted that the long duration exposure even to low levels of pesticides could create a significant impact at population level. Hence, earthen dykes need to be built to avoid agricultural runoff entering the Sanctuary and also help to hold sufficient amount of water for breeding birds.

Estimating biotransformation rate constants of organic chemicals from modeled and measured elimination rates

In this study, biotransformation rate constants are estimated for a large set of organic compounds. Biotransformation (km) is considered part of the total elimination, further consisting of physico-chemical elimination to water (kw), depuration by feces (kf) and growth dilution (gamma). Existing models are used to estimate kw and kf, and gamma. The difference between measured elimination rate constants and the sum of predicted elimination rate constants for water, feces and growth indicates the ration of biotransformation in the total elimination. In all examined animal classes, polycyclic aromatic hydrocarbons seem to be metabolized at an intermediate rate. Because of the relative low hydrophobicity of some of the studied compounds, their physico-chemical elimination rate constant is relatively high, and the relative contribution of metabolism to total elimination of these compounds is therefore relatively low. Fish seem to be capable of metabolizing chlorodibenzo-p-dioxins and -furans, DDT, chloroanilines and phenol.

Dieldrin poisoning and botulism in Australian pelicans (Pelecanus conspicillatus)

Autopsies and laboratory examinations of material from 24 Australian pelicans found sick or dead in southern coastal Queensland in 1977 to 1979 revealed dieldrin poisoning in 8 from the Brisbane region and botulism in 8 from Brisbane, Bundaberg and Gladstone. In those diagnosed as dieldrin poisoning, brain and liver samples contained 12.1 to 27.4 and 34.0 to 48.1 mg/kg dieldrin respectively. All of these birds were emaciated, 2 had convulsed and 1 had muscle tremors. Low and probably insignificant residues of DDE were detected in many birds. Type C botulism was confirmed in 4 of the 6 birds tested with specific antiserums. A large number of parasites including mites, lice, nematodes, cestodes, trematodes, coccidia and Sarcocystis sp were found but were thought to have had only a limited effect on the health of these birds.

Metabolism and route of excretion of the chloro-cyclodiene HCE in the pigeon

Male feral pigeons were fitted with re-entrant bile duct cannulae, or were colostomized to facilitate the separate collection of urine and feces. After administration of 15 mg kg(-1) of [14C]-HCE by intraperitoneal injection, collections of bile and urine were made to determine the routes of excretion and the major metabolites. Within seven hrs the percentages of injected 14C excreted were 16.2 2.9% in the urine of colostomized birds and 12.8 1.1% in the bile of cannulated birds. Since the rate of elimination of 14 C in the feces of colostomized birds was very low (29% dose in 12 days) compared with 59% in urine, apparently some biliary metabolites were reabsorbed from the gut prior to elimination in urine. Nearly all excreted material was in conjugated form. Biliary conjugates were predominantly glucuronides (greater than 84% of total 14C) whereas 96% of the conjugated material in urine was sulfate. Initial metabolism was predominantly oxidative with the formation of a monohydroxy epoxide (HHC), which was subsequently converted into two secondary metabolites (endo-HHC and dihydroxy-HCE). In contrast to other species, no measurable quantity of trans-diol was formed. The same pattern of initial metabolism was found in hepatic microsomes. The metabolism and excretion of HCE is slower in the pigeon than in the male rat, thus providing further evidence for the limited capability of the species to perform certain detoxifying transformations.

Perspectives of the chemical fate and toxicity of pesticides

The wide-spread use of pesticides in modern agriculture has created a need to investigate the chemical transformation of pesticides in plants and animals. This paper reviews the chemical and biochemical fate of various pesticides and other xenobiotics. Photochemical mechanisms appear to be the most common pathways for the abiotic transformation of these chemicals. Biotic transformation includes a large group of biochemical reactions which may result in either deactivation (detoxication) or activation (toxication) of bioactive compounds. The need for quality control in the production of pesticides is also discussed.